(II) Phycoremediation Using Scenedesmus Obliquus: Cell Physicochemical Properties, Biochemical Composition and Metabolomic Pro Ling
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Mechanisms of Lead (II) Phycoremediation Using Scenedesmus Obliquus: Cell Physicochemical Properties, Biochemical Composition and Metabolomic Proling Danouche M. ( [email protected] ) Moroccan Foundation for Advanced Science https://orcid.org/0000-0003-1654-8372 El Ghachtouli N Sidi Mohamed Ben Abdellah University Aasfar A Moroccan Foundation for Advanced Science Bennis I. Moroccan Foundation for Advanced Science El Arroussi H. Moroccan Foundation for Advanced Science Research Keywords: Scenedesmus obliquus, Pb(II)-phycoremediation mechanism, Cells physicochemical properties, Biochemical composition, Metabolomic proling. Posted Date: July 9th, 2021 DOI: https://doi.org/10.21203/rs.3.rs-679604/v1 License: This work is licensed under a Creative Commons Attribution 4.0 International License. Read Full License 1 Mechanisms of lead (II) phycoremediation using Scenedesmus obliquus: cell 2 physicochemical properties, biochemical composition and metabolomic 3 profiling 4 Danouche M.a, b*, El Ghachtouli N.b, Aasfar A.a, Bennis I.a, El Arroussi H.a,c 5 a Green Biotechnology Center, Moroccan Foundation for Advanced Science, Innovation and 6 Research (MAScIR), Rabat, Morocco. 7 b Microbial Biotechnology and Bioactive Molecules Laboratory, Sciences and Technologies 8 Faculty, Sidi Mohamed Ben Abdellah University, Fez, Morocco. 9 c AgroBioScience (AgBS), Mohammed VI Polytechnic University (UM6P), Ben Guerir, Morocco. 10 *Corresponding author: 11 Phone: +212 633 541 908 12 E-mail: [email protected] (Danouche), [email protected] (El Arrousi) 13 Abstract 14 This study highlights the mechanisms involved in Pb(II)-phycoremediation using the Pb(II) 15 tolerant strain of Scenedesmus obliquus. Firstly, monitoring of cell growth kinetics in control and 16 Pb(II)-doped medium revealed a significant growth inhibition, while the analyses through flow 17 cytometry and Zetasizer revealed no difference in cell viability and size. Residual weights of 18 control and Pb(II)-loaded cells assessed by thermogravimetric analysis, were 31.34% and 57.8%, 19 respectively, indicating the uptake of Pb(II) into S. obliquus cells. Next, the use of chemical 20 extraction to distinguish between the intracellular and extracellular uptake indicated the 21 involvement of both biosorption (85.5%) and bioaccumulation (14.5%) mechanisms. Biosorption 22 interaction of the cell wall and Pb(II) was confirmed by SEM, EDX, FTIR, zeta potential, zero- 23 charge pH, and contact angle analyses. Besides, the biochemical characterization of control and 1 24 Pb(II)-loaded cells revealed that the bioaccumulation of Pb(II) induces significant increases in the 25 carotenoids and lipids content and decreases in the proportions of chlorophyll, carbohydrates, and 26 proteins. Finally, the metabolomic analysis indicated an increase in the relative abundance of fatty 27 acid methyl esters, alkanes, aromatic compounds, and sterols. However, the alkenes and 28 monounsaturated fatty acids decreased. Such metabolic adjustment may represent an adaptive 29 strategy, that preventing high Pb(II)-bioaccumulation in cellular compartments. 30 Keywords: Scenedesmus obliquus; Pb(II)-phycoremediation mechanism; Cells physicochemical 31 properties; Biochemical composition; Metabolomic profiling. 32 Introduction 33 Since the formation of the Earth, nearly all of the heavy metals (HMs) that we know today 34 have been naturally present in trace amounts and have been recycled biogeochemically between 35 the environmental compartments (Garrett 2000). However, with global expansion, anthropogenic 36 activities, including mining, excessive use of fertilizers in agriculture, and mismanagement of 37 hazardous wastes, have resulted in an increase of the inorganic pollution of water and soil (Ashraf 38 et al. 2014). Because they are not biodegradable, HMs can persist in ecosystems and can 39 bioaccumulate into organisms of different trophic levels, causing various signs of toxicity to all life 40 forms, including humans (Yan et al. 2018). Mercury (Hg(II)), cadmium (Cd(II)), lead (Pb(II)), 41 arsenic (As(III)), and chromium (Cr(VI) are recognized as the most harmful pollutants (Kumar et 42 al. 2015). The maximum contamination limits of these metals are 0.002, 0.005, 0.015, 0.01, and 43 0.1 mg L-1, respectively (USEPA 2016). Unfortunately, their actual concentrations in industrial 44 effluents generally exceed these standards requiring an adequate treatment before their release into 45 the environment (Selvi et al. 2019). Thus, the exposure to Pb(II) results in a wide range of toxic 46 effects on the physiological, biochemical and metabolic functions of exposed organisms 47 (microorganisms, aquatic plants and animals), as well as human health complications resulting 2 48 from direct exposure or consumption of contaminated food or water (Lee et al. 2019). Indeed, 49 various techniques, including precipitation, adsorption, nanofiltration, ultrafiltration, reverse 50 osmosis, electrochemical technologies, and biological approaches have been applied to remove 51 HMs from contaminated water bodies (Kumar et al. 2015). 52 Bioremediation approaches are competitive to conventional physical-chemical procedures as 53 they are efficient, environmentally friendly and inexpensive (Chibueze et al. 2016). The application 54 of microalgae in wastewater treatment (phycoremediation) has recently emerged as a promising 55 solution because of its advantages over other bioremediation methods (Jais et al. 2017; Wollmann 56 et al. 2019). Although several studies have documented the potential application of 57 phycoremediation for the removal of Pb(II) from contaminated water. The majority of these studies 58 have highlighted the application of inactive biomass of microalgae species as biosorbent without 59 considering the application of growing cells (Flouty and Estephane 2012). 60 Despite the advantages of using growing cells over biosorbent biomass, only a few studies 61 have described the potential application of live microalgae for the removal of Pb (II) from 62 contaminated water (Liyanage et al. 2020; Pham et al. 2020; Piotrowska-Niczyporuk et al. 2015). 63 It avoids the steps of cultivation, harvesting, drying, pre-treatment and conservation of biomass 64 before it is used as a biosorbent (Malik 2004). Also, the use of growing cells of HMs-tolerant 65 microalgae strains will further enhance the removal efficiency by the mean of both metabolism- 66 independent (Biosorption) and metabolism-dependent (Bioaccumulation) mechanisms (Kumar et 67 al. 2015). On the oher hand, under metal stress conditions, living microalgae produce various 68 valuable substances such as polymers, proteins, pigments and lipids (Liu et al. 2016). Which offers 69 a real opportunity to operate in a variety of industrial sectors, especially lipids, as a source of third- 70 generation biofuels (Randrianarison and Ashraf 2017). Understanding the influence of HMs on the 3 71 biochemical composition of green microalgae is critical for a targeted valorization of the biomass 72 and/or the metabolites produced during the phycoremediation process. 73 The aim of this study was to examine the mechanisms involved in Pb (II) phycoedimentation 74 using live S. obliquus, and to investigate the changes in physicochemical properties, biochemical 75 composition, and metabolomic profiling of the cells before and after Pb (II) phycoedimentation. 76 Methods/experimental 77 Strain and culture condition 78 The green alga S. obliquus used in this study has been previously selected as a Pb(II)-tolerant 79 strain (Danouche et al. 2020). Its pure culture was sub-cultured at regular times in BG11 medium 80 (1.5 g NaNO3, 40 mg K2HPO4, 36 mg CaCl2 2H2O, 6 mg ammonium citrate monohydrate, 6 mg 81 ammonium ferric citrate, 1 mg ethylenediaminetetraacetic acid (EDTA), 2.86 mg H3BO3, 1.81 mg 82 MnCl2 4H2O, 0.22 mg ZnSO4 7H2O, 0.39 mg NaMoO4 5H2O, 0.079 mg CuSO4 5H2O, 0.050 mg 83 CoCl2 6H2O in 1 L of distilled water) (Allen 1968). Experiments were performed with a pre-culture 84 of S. obliquus obtained at the exponential phase. The biomass was firstly recovered by 85 centrifugation at 4700 rpm for 10 min. Then, the pellet was diluted in Erlenmeyer flasks containing 86 100 mL of BG11 medium for negative control and Pb(II)-doped medium at the concentration of -1 87 EC50 = 141 mg L corresponding to the half-maximal effective concentration (Danouche et al. 88 2020). The initial optical density (OD) of all experiments was adjusted to 0.350 ± 0.025 at A680nm 89 using Ultrospec™ 3100 pro UV-Visible spectrophotometer, corresponding to 2 x 106 cells mL-1 90 equivalent. Flasks were incubated for 23 days under controlled conditions at 25 ± 2 ºC, under rotary 91 shaking conditions at 150 rpm, and 10 h:14 h light-dark cycle. 92 Growth inhibition, cells viability and size analysis 93 Growth inhibition: the growth kinetics of S. obliquus in control and Pb (II)-doped medium 94 were monitored spectrophotometrically at two-day intervals. The linear relationship between 4 95 microalgal density (N, in cells per milliliter) and OD680 was determined as reported by Zhou et al. 96 (2012) using CKX41 Olympus light microscope and a Malassez counting chamber with a depth of 97 0.2 mm. The calibration curve was as eq (1): 98 Y= 7. 106 X + 2083 (R² = 0.98) eq (1) 99 Where Y is the number of cells (C mL-1) and X denotes the OD at 680 nm. The specific growth 100 rate (SGR) (μ, in day-1) was calculated in the exponential phase using eq (2), as described by 101 Aguilar-Ruiz et al. (2020). 102 eq (2) Ln X2 − Ln X1 휇 = 푡2−푡1 103 Where µ is the growth rate and X2, X1 represent the microalgal biomass concentration at t2 and t1 104 (time), respectively. 105 Cells viability: Pb(II) effect on the viability of S. obliquus was evaluated as described by da 106 Silva et al. (2009). An amount of 106 cells from both control medium BG11 and Pb (II) doped 107 medium were centrifuged at 4700 rpm for 10 min, the pellet was then washed with phosphate buffer 108 solution (PBS, pH 7.0). Thus, the cells were exposed to 10 µg mL-1 of propidium iodide (PI, Ref 109 81845 FLUKA) for 10 min in the dark and was directly analyzed by BD FACSCalibur Flow 110 Cytometry (FCM) System (BD Biosciences).